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SU0004617_SSNL
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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E
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88 (STATE ROUTE 88)
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18327
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2600 - Land Use Program
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PA-0300569
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SU0004617_SSNL
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Last modified
11/20/2024 9:22:00 AM
Creation date
9/4/2019 6:18:59 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0004617
PE
2611
FACILITY_NAME
PA-0300569
STREET_NUMBER
18327
Direction
E
STREET_NAME
STATE ROUTE 88
City
CLEMENTS
APN
01922026
ENTERED_DATE
8/24/2004 12:00:00 AM
SITE_LOCATION
18327 E HWY 88
RECEIVED_DATE
2/10/2004 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\E\HWY 88\18327\PA-0300569\SU0004617\SS STDY.PDF
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EHD - Public
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t <br /> As noted from the table, in the months of January, February, March, November and December, <br /> deep percolation probably will occur. During these months, it is critical.that nitrogen not be <br /> applied to lawns and landscaping, not only because of deep percolation,but also since most plants <br /> are in dormancy and there will be little uptake. <br /> In addition, if the leachlines can be installed as high in elevation as possible, during the months of <br /> April through October, significant evapotranspiration may occur to alleviate excessive percolation <br /> of septic effluent. This premise would not only apply to surface and subsurface soil temperatures <br /> causing evaporation, but also to transpiration by certain plants that are planted near, or over the <br /> leachfield. These would include grasses and shallow rooted shrubs over the leachfield. <br /> C. GROUNDWATER INFORMATION <br /> L. ESTIMATED GROUNDWATER GRADIENT AND VELOCITY <br /> According to the most recent Groundwater Lines of Equal Depth Map (1999) provided by the San <br /> Joaquin County Flood Control District, the static water level under the center of the project is <br /> approximately 140 ft below grade.. Lines of Equal Elevation maps are included in Appendix 6 to <br /> illustrate the groundwater directional flow during the years of 1992, 1996, 1997, 1998, and 1999. <br /> As noted the directional flow appears to have changed over these years, but is predominately <br /> toward the Mokelumne River. Whether the gradient under the subject property flows <br /> northwesterly toward the River, or if it continues in a westerly direction to eventually encounter <br /> the River is unknown without highly sophisticated monitoring over time. Groundwater typically <br /> follows the topography of the land surface. Consequently, as denoted from the USGS <br /> topographical map, the flow direction may be in a predominate westerly direction until the <br /> influence of the River overtakes gravitational flow. The equal lines map show the gradient to be <br /> very gradual and flat as the groundwater flow travels west-southwest toward the town of <br /> Lockeford. <br /> The groundwater gradient as the flow descends from the project site is estimated to be 10 ft <br /> 7,920 ft (1.5 mi) = 0.00126 ft/ft, based on the equal elevation and depth maps. The velocity of <br /> the groundwater directly downgradient from the subject site can be estimated by the following <br /> formula: <br /> K (h, h2) <br /> Vaquifer L <br /> 7.5 p <br /> 3, <br /> Where: <br /> K=Hydraulic conductivity of aquifer formation in gals/day/ft, 5000 gals/day/ft2 (est. based on a silty, <br /> { medium sand formation) <br /> h,= 140 ft <br /> h,= 130 ft <br /> �i <br /> L-= 1.5 mi =7,920 ft <br /> p =porosity of aquifer 37% (est) <br /> i. <br /> Vnquif,=2.3 ft/day -- - <br /> { <br /> ' Page -8- <br /> Chesney Consulting <br />
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